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Zbornik radova Koridor 10 - Kirilo Savić

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3rd International Scientific and Professional Conference<br />

CORRIDOR <strong>10</strong> - a sustainable way of integrations<br />

periodically taken by a specialised waste-treatment team and disposed. Glass fibres and styrophore<br />

material that are used for insulation purposes can be recycled by removing them safely and reselling<br />

them to various users. Others such as chemicals, paints and oil-mixed sludges are collected by the by<br />

authorized organizations’ hazardous waste management unit and stored in a specialised storage area.<br />

Liquid wastes<br />

Liquid wastes are generally bilge and ballast waters contaminated by oil and various chemicals. Bilgewater<br />

in engine rooms can be further mixed with fuel and oil. They belong to the category of oily<br />

waste, often contaminated with oil and cargo residues together with other pollutants, such as -<br />

inorganic salts, metals, such as arsenic, copper, chromium, lead and mercury [9-11]. The composition<br />

of the water can be very different, depending on the type of vessel from which comes. Occasionally,<br />

oily waste is spilled into the aquatic environment during the scrapping process and the water around<br />

the yards may be polluted.<br />

The collected oily wastes are carried to certificated reprocessing companies or to a specialised facility<br />

for disposal and the domestic wastes of the vessels are collected in the cesspools of the shipbreaking<br />

yards, and later are transported to the sewage treatment plants.<br />

Atmospheric pollutants<br />

The most important atmospheric pollutant of shipbreaking activities is the asbestos. If not properly<br />

disposed, it can form a cancerogenic powder. The usual way is to disassemble asbestos linings by<br />

wetting and removing them in bulk. Present asbestos removal facility and team for the removal of this<br />

material have greatly reduced the risk of this mode of pollution. Disassembling of air conditioning and<br />

refrigeration systems can also result in the release of refrigerant chloro-fluoro carbon series chemicals<br />

that are hazardous to the ozone layer. Some shipboard fire extinguishing systems can also be the<br />

source of such gases. The availability of licensed companies for this activity implies an improved<br />

capacity for this hazardous waste in the local area. Another source of atmospheric pollutants is the<br />

practice of stripping the electrical cables off their insulation by burning: plastic material used for<br />

insulation is a source of highly toxic gases such as dioxins, polychromatic hydrocarbons, etc. [12].<br />

Apart from the atmospheric pollution, flammable gases from fuel or oil tank residues become highly<br />

explosive if mixed with air in certain proportions. Therefore, proper gas freeing and gas monitoring<br />

procedures have to be followed before a ship is broken. Greenpeace has reported several fatal<br />

accidents in the past [12].<br />

Heavy metal pollution of water area<br />

Data from various sources show a high concentration of heavy metals at the site of vessels'<br />

dismantling. For example, a study has also been carried out at a similar shipbreaking location at<br />

Alang, India. It has been reported that at a near shore station near Alang, concentrations of Fe, Mn,<br />

Co, Cu, Zn, Pb, Cd, Ni and Hg are 25-15, 500% higher when compared to another control station at<br />

the surroundings [13].<br />

The group of marine ecologists and chemists from the Dokuz Eylul University Institute of Marine<br />

Sciences and Technology in Turkey conducted a study by taking samples from the location close to<br />

the shipbreaking yards. Results of this study showed that Al and Fe are above their normal levels due<br />

to the existence of shipbreaking and steel industry ashore. Also Cd, Ni and Zn at the surface water<br />

were found to be higher than the normal levels [14].<br />

3. DISPOSAL AND RECYCLING<br />

The waste/material stream following demolition is distributed and transported out of the dismantling<br />

site to local enterprises for re-sale, re-manufacturing or recycling. These enterprises are usually<br />

located within the vicinity of the dismantling facility and are often under the same or related ownership.<br />

Re-sale:<br />

The trade of recovered usable items may be found in the vicinity of the scrapping facilities or items<br />

may be transported to central areas (main cities) for re-sale. The individual trade facilities tend to<br />

Belgrade, 2012 286

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